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Invasive Chinese Pond Mussel Sinanodonta Woodiana Threatens Native Mussel Reproduction by Inducing Cross‐Resistance of Host Fish

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Invasive Chinese Pond Mussel Sinanodonta Woodiana Threatens Native Mussel Reproduction by Inducing Cross‐Resistance of Host Fish Received: 13 June 2016 Revised: 15 November 2016 Accepted: 8 January 2017 DOI 10.1002/aqc.2759 RESEARCH ARTICLE Invasive Chinese pond mussel Sinanodonta woodiana threatens native mussel reproduction by inducing cross‐resistance of host fish Seth W. Donrovich1 | Karel Douda1 | Věra Plechingerová1 | Kateřina Rylková1 | Pavel Horký1 | Ondřej Slavík1 | Huan‐Zhang Liu2 | Martin Reichard3 | Manuel Lopes‐ Lima4,5 | Ronaldo Sousa6 1 Department of Zoology and Fisheries, Czech University of Life Sciences Prague, Prague, Abstract Czech Republic 1. The effects of invasive alien species (IAS) on host–affiliate relationships are often subtle and 2 The Key Lab of Aquatic Biodiversity and remain unnoticed or insufficiently quantified. The global decline of freshwater unionid mussel Conservation, Institute of Hydrobiology, species has been attributed to many causes, but little is known about the interactions of IAS, Chinese Academy of Sciences, Wuhan, China with their complex life cycle, which includes an obligatory parasitic stage (the glochidium) that 3 Institute of Vertebrate Biology, Academy of develops on fishes. Sciences of the Czech Republic, Brno, Czech Republic 2. The capacity of a European freshwater mussel, Anodonta anatina, to develop on its widespread 4 CIBIO/InBIO ‐ Research Center in fish host, Squalius cephalus was tested experimentally, after previous infestations by the IAS, Biodiversity and Genetic Resources, University Sinanodonta (Anodonta) woodiana. The initial attachment of glochidia, the length of the parasitic of Porto, Vairão, Portugal period, and the metamorphosis success rate of A. anatina glochidia were compared among 5 CIIMAR/CIMAR ‐ Interdisciplinary Centre of Marine and Environmental Research, treatments of different priming infestation intensities. University of Porto, Matosinhos, Portugal 3. The metamorphosis success rate of the native A. anatina glochidia was strongly reduced 6 – CBMA Centre of Molecular and (Wilcoxon Signed‐Rank Test, P < 0.001) and declined by 42.1 and 45.4% on fish hosts that Environmental Biology, Department of Biology, University of Minho, Braga, Portugal were previously exposed to S. woodiana by single and multiple priming infestations, respec- ‐ Correspondence tively, in comparison with the control group. Such cross resistance is expected to decrease sig- Karel Douda, Czech University of Life Sciences nificantly the quality of the host resources available to native mussels. Prague, Department of Zoology and Fisheries, 4. This study provides the first evidence of the host‐mediated adverse impact of invasive Kamýcká 129, Prague, CZ 165 00, Czech Republic. S. woodiana on native mussel species. These results also highlight the importance of potential Email: [email protected] competition for hosts between threatened groups of affiliate species and their invasive coun- Funding information terparts, which should be reflected in conservation strategies. Czech Science Foundation, Grant/Award Number: 13‐05872S KEYWORDS adaptive immunity, Anodonta anatina, competition, freshwater, glochidia, host–parasite relationships, invasive alien species 1 | INTRODUCTION may impair several ecosystem functions because these species have high filtration rates, providing an important link between the water The abundance and diversity of freshwater mussels are severely column and the benthic zone, and also playing an important role in decreasing worldwide, with nearly half of the species currently nutrient cycling, substrate stability, bioturbation, and controlling threatened. This situation may have profound consequences at sev- the levels of suspended solids (Bauer & Wachtler, 2001; Bogan, eral ecological levels, from individuals to ecosystems (Bogan, 1993; 1993; Lopes‐Lima et al., 2017; Vaughn & Hakenkamp, 2001; Burlakova et al., 2011; Lopes‐Lima et al., 2014; Walker, Jones, & Williams, Warren, Cummings, Harris, & Neves, 1993). In addition, Klunzinger, 2014). For example, the decline of freshwater mussels freshwater mussels are usually considered suitable bioindicators of Aquatic Conserv: Mar Freshw Ecosyst. 2017;1–9.wileyonlinelibrary.com/journal/aqc Copyright © 2017 John Wiley & Sons, Ltd. 1 2 DONROVICH ET AL. overall ecosystem health and are also thought to be keystone spe- suggested that particular mussel species can compete for host cies, as they increase species richness and overall biodiversity resources by inducing cross‐resistance of host fish (Dodd, Barnhart, when present in an ecosystem (Aldridge, Fayle, & Jackson, 2007; Rogers‐Lowery, Fobian, & Dimock, 2005; Strayer, 2008). Competi- Spooner et al., 2013). tion for host fish is most likely a common and natural mechanism Although the reasons for freshwater mussel decline are numer- in freshwater mussel assemblages (Strayer, 2008). However, it could ous and idiosyncratic, one of the causes of most concern is related have detrimental consequences for native mussel species when to the introduction (deliberate or accidental) of invasive alien species induced by IAS. (IAS). The number of freshwater IAS has been increasing rapidly in There is only limited knowledge on the specific impacts that both tropical and temperate latitudes and rigorous studies of the invasive mussels have on native mussels with regard to competition impacts of IAS are often lacking (Tricarico, Junqueira, & Dudgeon, for host fish. In this context, one of the most potentially hazardous 2016). It is supposed that introductions of other freshwater bivalves species is Sinanodonta (Anodonta) woodiana (Lea 1834), commonly are particularly problematic for native freshwater mussels (Baker & known as the Chinese pond mussel. Sinanodonta woodiana is native Levinton, 2003; Ricciardi, Neves, & Rasmussen, 1998; Sousa, Novais, to two river basins in China, the Yangtze and Amur rivers, where it Costa, & Strayer, 2014; Sousa, Pilotto, & Aldridge, 2011). The intro- was primarily located before its expansion to different parts of the duction of bivalve species can lead to competition with native spe- world, including Southeast Asia, Europe, North America, and the cies for space, nutrients, food, and possibly also for host fish, the Caribbean (Kraszewski, 2007; Watters, 1997; Zieritz et al., 2016). latter of which are necessary for completion of the freshwater mus- This species is spreading quickly throughout European waters and sel life cycle (Arey, 1932; Barnhart, Haag, & Roston, 2008; Kat, has reached high densities in many rivers and standing water bodies, 1984; Novais, Dias, & Sousa, 2016; Sousa et al., 2014). such as the Cris/Koros River basin in Romania and Hungary Unionid freshwater mussels produce parasitic larvae (glochidia) (Sarkany‐Kiss, 1997; Sarkany‐Kiss, Sirbu, & Hulea, 2000), Lake that must attach to fish to complete their development into juve- Balaton in Hungary (Benkő‐Kiss, Ferincz, Kováts, & Paulovits, niles (Dillon, 2000). To form a successful host fish and freshwater 2013), the Danube and Tisza rivers in Hungary (Bódis, Tóth, & mussel relationship, three conditions are required: initial contact Sousa, 2014, 2016), lowland rivers in Serbia (Paunovic, Csányi, Simic, between glochidia and the host fish, physiological suitability of Stojanovic, & Cakic, 2006) and the Czech Republic (Douda, Vrtílek, the host for attachment and glochidia development, and resistance Slavík, & Reichard, 2012), channels with soft substrate in Italy of the glochidia to the host’s immune responses (Neves, Weaver, (Cappelletti, Cianfanelli, Beltrami, & Ciutti, 2009), inter‐basin water- & Zale, 1985). In each reproductive year, many glochidia are ways in the Iberian peninsula (Pou‐Rovira et al., 2009), and warmer released, so the first factor is dependent on the distinct infestation water bodies in Poland (Kraszewski & Zdanowski, 2007). Reproduction strategies of the mussels (Barnhart et al., 2008), ecosystem condi- in S. woodiana occurs in autumn and the glochidia are released in tions, fish microhabitat preferences, fish behaviour and fish abun- summer in European waters (Douda et al., 2012; Sarkany‐Kiss et al., dance. If the glochidia fail to attach to a host fish, they will 2000) to begin parasitic life on a host for a period that varies accord- eventually sink to the substrate, where opportunities for attach- ing to environmental conditions, mainly water temperature ment are highly unlikely and the glochidia perish (Jansen, Bauer, (Afanasjev, Zdanowski, & Kraszewski, 2001). Sinanodonta woodiana & Zahner‐Meike, 2001). Unsuccessful infestations can take place produce glochidia two or three times per year (Sarkany‐Kiss et al., either when the host fish contains insufficient chemical or nutri- 2000) in high numbers (Wachtler, Dreher‐Mansur, & Richter, 2001) tional requirements for metamorphosis to occur or as a result of and successfully parasitize a wide spectrum of European native fish direct immune system rejection by the host fish (Neves et al., species (Douda et al., 2012). 1985). In these cases, glochidia may fail to become encysted or The aim of this study was to quantify the capability of a native are sloughed off before transformation (Jansen et al., 2001). Alter- European fish to host native mussel glochidia following previous natively, failure to metamorphose may result from the glochidia infestation by the invasive S. woodiana. The null hypothesis tested being abnormally encysted before detachment (Arey, 1932; was that a priming infestation by an invasive unionid mussel has Rogers‐Lowery, Dimock, & Kuhn, 2007). no detectable effect on the subsequent development of native The fish immune
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